the impact of turkish manufacturing industry on co2 …
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LAÜ Sosyal Bilimler Dergisi (VIII-II) EUL Journal of Social Sciences
Aralık 2017 December
LAÜ Sosyal Bilimler Dergisi (VIII-II): 150-167
THE IMPACT OF TURKISH MANUFACTURING INDUSTRY
ON CO2 EMISSIONS
TÜRKİYE’DE İMALAT SANAYİ SEKTÖRÜNÜN CO2 EMİSYONU ÜZERİNE ETKİSİ
Zeliha ÖZDEMİR Asst. Prof. Dr. Demet Beton KALMAZ
European University of Lefke European University of Lefke
MBA graduate Department of Economics
[email protected] [email protected]
Received 5 May 2017- Accepted 22 August 2017
Gönderim 5 Mayıs 2017- Kabul 22 Ağustos 2017
Abstract: Global warming has emerged as a result of human activities, and greenhouse gases are
the most effective cause of global warming. The accumulations of greenhouse gases have rapidly
increased in the atmosphere as a result of the increase in use of fossil fuels, wrong use of land, and
industrialization. The aim of the study is to examine the relationship between carbon dioxide
emissions, electricity consumption, economic growth, and trade openness on manufacturing
industry in Turkey by using time series data between the years 1962 and 2013. The study employs
the bound test for ARDL approach, ECM, Granger causality test and Cusum and Cusumsq test.
CO2 emissions are high due to two reasons in Turkey. First, Turkey’s energy intensity is high.
Second, electricity production depends on non-renewable sources. Turkey should decrease energy
intensity while increasing the share of renewable energy sources for energy production to be able to
decrease energy CO2 emissions in the manufacturing industry.
Keywords: CO2 emissions, electricity consumption, trade, ARDL
Öz: Günümüzün en önemli sorunlarında biri haline gelen küresel ısınma insan faaliyetleri sonucu atmosferde bulunan sera gazlarının artması sonucu ortaya çıkmıştır. Küresel ısınmanın en önemli
sebebi olan sera gazlarının atmosferde artması özellikle sanayi devrimi ile birlikte fosil yakıtlarına olan talebin artmasına ve yanlış arazi kullanımına bağlanmaktadır. Atmosferde bulunan sera
gazları içerisinde küresel ısınmaya en fazla etki eden 𝑪𝑶𝟐 emisyonudur. Türkiye'de bulunan imalat
sanayi sektörleri üzerinde yapılan bu çalışmanın amacı, karbondioksit emisyonları, elektrik tüketimi, ekonomik büyüme ve imalat sanayi sektöründeki ticaret açıklığı arasındaki ilişkiyi 1962
ve 2013 yılları arasında, zaman serisi verilerini kullanarak incelemektir. Araştırmada, ARDL sınır testi yaklaşımı, hata düzeltme modeli, Granger nedensellik testi, ve cusum ve cusumsq testi
uygulanmıştır. Türkiye'de 𝑪𝑶𝟐 emisyonunun yüksek olmasının iki nedeni vardır. Birincisi,
Türkiye'nin enerji yoğunluğunun yüksek olması, ikincisi ise Türkiye’de elektrik üretiminin büyük
bir bölümünün yenilenemez enerji kaynaklarına bağlı olmasıdır. Bu nedenle, Türkiye’de 𝑪𝑶𝟐
emisyonlarını azaltabilmek için enerji üretiminde yenilenebilir enerji kaynaklarının payı arttırılmalı ve imalat sanayinde enerji yoğunluğu azaltılmalıdır.
Anahtar Kelimeler: CO2 emisyonu, elektrik tüketimi, ticaret, ARDL
LAÜ Sosyal Bilimler Dergisi (VIII-II) EUL Journal of Social Sciences
Aralık 2017 December
Zeliha Özdemir, Demet Beton Kalmaz | 151
INTRODUCTION
Earth's atmosphere consists of various gases and these gases traps heat which
creates greenhouse effect. The increase of these atmospheric gases causes the
problem of global warming. Since these gases create greenhouse effect, they are
called greenhouse gases (GHG). Global warming, which arises as a result of GHG, is
one of the main concerns of the recent scientists and policy makers. Global warming
is the increase of the temperature of land, sea and air (Dincer, 2000). As the global
warming increases, the sea level rises and the glaciers melt. The risk of flood
increases.
GHG consist of carbon dioxide (CO2), methane (CH4), nitrous oxide (N2O),
chlorofluorocarbons (CFC), hydrofluorocarbons (HCFC) and Sulphur hexafluoride
(SF6). Table 1 represents the properties of the GHG in the atmosphere.
Table 1: Properties of GHG
GHG
Anthropogenic
Sources
Concentration
(parts per
billion)
Global
Warming
Potential
(GWP)
Lifetime in
Atmosphere
(year)
Carbon Dioxide
(CO2)
Fossil-fuel combustion,
Cement production Land-
use conversion,
280,000
1
100
Methane
(CH4)
Fossil-fuel, Rice paddies,
Waste dumps 700 25 12
Nitrous Oxide
(N2O) Fertilizer, Combustion,
Industrial processes 270 298 114
Chlorofluoroca
rbons (CFC) Liquid coolants, Foams 0,534 10,900 100
Hydrofluorocar
bons (HCFC) Refrigerants 0,218 1,810 12
Sulphur
Hexafluoride (SF6) Dielectric fluid 0,00712 22,800 3,200
Source: Center for Climate and Energy Solutions, 2017
*Global Warming Potential for 100-time horizon.
In the first column of Table 1, the names of GHG in atmosphere are given,
followed by a column giving information about the anthropogenic sources of the
GHG. The third column influences the concentration of each GHG which influences
the intensity of gases in the atmosphere. Fourth column represents the global
warming potential (GWP) of the related GHG, and finally in the last column gives
the information for how long the gas remains in the atmosphere as measured in years.
Carbon Dioxide (CO2) occurs as a result of fossil-fuel combustion, cement
production and land use conversion. Atmospheric concentration of CO2 is 280,000
per billion. GWP is taken as constant in CO2 and it remains 100 years in atmosphere.
Methane (CH4) is caused by fossil-fuels, rice paddies and waste dumps. From Table
1, it can be seen that a CH4 gas has twenty five times GWP more than CO2.
Atmospheric concentration of CH4 is 700 per billion and lifetime is 12 years in
LAÜ Sosyal Bilimler Dergisi (VIII-II) EUL Journal of Social Sciences
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152 | The Impact of Turkish Manufacturing Industry on CO2 Emissions
atmosphere. Nitrous Oxide (N2O) comes from fertilizers, fossil-fuel combustion and
industrial processes. Table 1 shows that N2O has 298 times GWP more than CO2.
N2O remains for 114 years and its concentration is 270 per billion in atmosphere.
Chlorofluorocarbons (CFC) consist of liquid coolants and foams. CFC atmospheric
concentration is 0,534 per billion. CFC has 10,900 times GWP more than CO2 and
remains 100 years in the atmosphere. Hydrofluorocarbons (HFCF) is a refrigerant
gases, it has 1,810 times GWP more than CO2. Atmospheric concentration of HFCF is 0,218 per billion and it remain 12 year in atmosphere. The last listed Sulphur
Hexafluoride (SF6) is used to cut the electricity. SF6 comes from dielectric fluid, SF6 22,800% times global warming potential more than CO2. Atmospheric concentration
of SF6 is 0,00712 per billion. SF6 has 3,200 years lifetime in atmosphere (Center for
Climate and Energy Solutions, 2017). All gases have heat-trapping effect but CO2 has highest heat-trapping ability among other GHG in the atmosphere (Özmen,
2009).
Turkey have growing rate of population and urbanization, so that Turkey’s
energy needs are increasing in all sectors (Bilgen et al., 2008). As the need for
energy is increasing, both energy consumption and energy production are also
increasing in Turkey. The increase of energy use increases also GHG generated in
Turkey. GHG generation of Turkey increased from 134,4 million tons to 340 million
tons between the years 1990 and 2015 (Turk Stat, 2017). Turkey contributes to more
GHG emissions during the production of energy process and this energy are mostly
used for manufacturing industry. Therefore, the impact of the economic variables
that causes CO2 emissions in Turkey is investigated in this study. This study will be
guidance for further research on topic and the results obtained from the empirical
analysis can be used to shape the environmental policies to decrease CO2 emissions
in Turkey.
1. LITERATURE REVIEW
The previous studies in literature related to the topic aimed to find the
relationship between CO2 emissions, energy consumption and economic growth
(Acaravcı & Ozturk, 2010; Pao et al., 2012; Al-mulali, 2011; Apergis & Payne,
2009; Bozkurt & Akan, 2014; Chang, 2010; Çoban & Kılınç, 2015; Ergün & Polat,
2015; Alam et al., 2012; Koçak, 2014; Lean & Smyth, 2010; Tiwari, 2011; Pao &
Tsai, 2010; Yavuz, 2014; Wang et al., 2011). In some studies in addition to those
variables FDI is also included (Altıntaş, 2013; Dinh & Shih-Mo, 2014; Öztürk & Öz,
2016; Tang & Tan, 2015). There are also studies adding trade openness instead of
FDI (Akın, 2014; Halıcıoğlu, 2009; Jalil & Mahmud, 2009; Keskingöz &
Karamelikli, 2015; Kivyiro & Arminen, 2014).
There are also studies focusing the causal interaction between CO2 emissions,
energy consumption, economic growth (Çoban & Kılınç, 2015) in Turkey. Some of
these studies included FDI as a control variable (Altıntaş, 2013; Öztürk & Öz, 2016),
while some added trade openness instead of FDI (Halıcıoğlu, 2009). There are also
studies adding employment ratio instead of trade openness (Öztürk & Acaravcı,
2010). Some studies found unidirectional causal relationship from energy
consumption to CO2emissions (Altıntaş, 2013; Çoban & Kılınç, 2015), while some
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studies estimated unidirectional causal relationship from economic growth to
CO2 emissions (Altıntaş, 2013). Some authors found bidirectional causality between
economic growth and CO2 emissions (Halıcıoğlu, 2009; Öztürk & Öz, 2016). Öztürk
& Acaravcı (2010) found no causal relationship among the variables. Some studies
applied only cointegration test on CO2 emissions and economic variables (Bozkurt &
Akan, 2014; Bozkurt & Okumuş, 2015; Çetin & Şeker, 2014; Keskingöz &
Karamelikli, 2015; Koçak, 2014; Yavuz, 2014). The results of those studies found
energy consumption, economic growth and CO2 emissions are cointegrated.
Table 2, summarizes some of the literature by giving the names of the authors,
the country studied, the sample used, model employed and the results found.
Table 2: Literature Review Summary
Authors Country Sample Variable Model Result
Acaravcı &
Öztürk (2010)
Nine
European
Countries
1960-2005
CO2 , EC ,EG
ARDL,
Granger Causality
Test
EG → CO2
EC → CO2
Adom et al.
(2012)
Ghana, Senegal
and
Morocco
1971-2007
CO2 , EG, TE,
IS
Bounds,
Granger Causality
Test
CO2 ↔ EG CO2 ↔ IS CO2 ↔ TE
Akbostancı et al.
(2009) Turkey 1968-2003
CO2, EG, POP
EKC,
Cointegration CO2 andEG
cointegration
Akın (
2014)
85 countries
1990-2011
CO2, EG, EC, TO
Cointegration,
Granger Causality
Test
CO2 → TO EG → CO2
EG → TO
Al-mulali (2011) MENA countries
1980-2009 CO2 , EG, EC Granger
Causality Test
CO2 ↔ EC CO2 ↔ EG
Al-mulali et al.
(2012) Seven region 1980-2008 CO2 ,UR, EC
Granger
Causality Test CO2 ↔ UR CO2 ↔ EC
Altıntaş (2013)
Turkey
1970-2008 CO2, EG, EC,
FDI
ARDL,
Granger Causality
Test
EG → CO2
EC → CO2
Anatasia
(2015)
Thailand Malaysia
1978-2008
CO2, EG, EC,
Export
Cointegration,
Granger Causality
Test
Export→ CO2
EG → CO2
EG → EC
Apergis & Payne
(2009)
Central America
1971-2004 CO2 , EG, EC,
EKC,
Granger Causality
Test
EC → CO2
EG → CO2
Ayeche et al.
(2016)
40 European
countries
1985-2014
EG, FD, TO,
CO2, EC, FDI, INF,
UR
ARDL,
Granger Causality
Test
EG ↔ FD EG ↔ TO
Aytun & Akın (2015)
Turkey 1971-2010 PSE, SSE,
TSE, CO2
Granger Causality Test
TSE→CO2
Bozkurt & Akan
(2014) Turkey 1960-2010 EC, CO2, EG
Cointegration
Test EC is positive
effect on CO2
Bozkurt &
Okumuş (2015)
Turkey
1966-2011
CO2, EG, EC, POP, TO
Cointegration
Test
All variable
cointegration
Chang
(2010)
China
1982-2004
CO2,EG , EC
Cointegration,
VECM ,Granger
Causality Test
EG → CO2
Cowan et al.
(2014)
BRICS
1990-2010
CO2, EG,
electricity
consumption
Granger
Causality Test
EG → CO2
electricity
consumption
→ CO2
Çetin & Sub Saharan 1985-2010 CO2 , EC, UR VECM, CO2 ↔ EC
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154 | The Impact of Turkish Manufacturing Industry on CO2 Emissions
Ecevit (2015) Countries Granger Causality
Test CO2 ↔ UR
Çetin & Seker (2014)
Turkey 1980-2010 CO2, EC, TO ARDL All variable
cointegration
Çetintaş &
Sarıkaya (2015)
USA and UK
1960-2004
CO2, EG, EC, TO, UR
Cointegration,
Granger Causality
Test
CO2→ EG EC → CO2
Çoban & Kılınç
(2015)
Turkey
1990-2012 CO2,
EG, EC
Cointegration,
Granger Causality
Test
EC → CO2
Dinh & Shih-Mo
(2014)
Vietnam
1980-2010 CO2, EC, EG,
FDI
Cointegration,
Granger Causality Test
CO2 ↔ EC
Dogan &
Turkekul (2016)
USA
1960-2010 CO2, EG, EC
, TO, UR
Cointegration,
Granger Causality
Test
CO2 ↔ EG
CO2 ↔ EC CO2 ↔ UR
Ergün & Polat
(2015)
30 OECD
countries
1980-2010
CO2, EC, EG
Cointegration,
Granger Causality
Test
EG → CO2
Halıcıoğlu (2009)
Turkey
1960-2005 CO2, EC,EG,
TO
ARDL,
Granger Causality
Test
CO2 ↔ EC CO2 ↔EG
Hossain (2011)
NIC
1971-2007 CO2, EC, TO, EG, UR
Cointegration,
Granger Causality Test
EC → CO2
TO → CO2
Hossain (2012)
Japan
1960-2009
CO2 , EG, EC, TO, UR
Cointegration,
Granger Causality
Test
CO2→ EG EC → CO2
Jalil & Mahmud
(2009)
China
1975-2005
CO2 , EG, EC, TO
EKC, Granger
Causality Test
EG → CO2
Kapusuzoğl
u
(2014)
Worldwide
OECD EU
Turkey
1960-208
CO2 , EG
Cointegration,
Granger Causality
Test
CO2→ EG
Kasman &
Duman
(2015)
New EU
member and
candidate countries
1992-2010
CO2, EC, EG, TO, UR
EKC, Granger
Causality Test
EC → CO2
EG → CO2
UR → CO2
TO → CO2
UR → TO
Katırcıoğlu
(2017)
Turkey
1960-2010
CO2, EC, EG,
Oil price
Cointegration
ECM,
Granger
Causality Test
EC → Oil
price
Katırcıoğlu,et al.
(2014)
Cyprus
1970-2009
CO2, EC, IT
Bounds test,
Granger Causality
test
CO2 ↔ EC IT→ CO2
EC →IT
Keskingöz
& Karamelikli (2015)
Turkey
1960-2011 CO2, EG, EC,
TO
ARDL
Import has
positive effect on CO2
Kivyiro &
Arminen (2014)
Six Sub
Saharan Africa
1971-2009
CO2, EG, EC, TO
ARDL,
Granger Causality
Test
CO2→ EG
Koçak (2014) Turkey 1960-2010 CO2, EG, EC ARDL EC positive
effect on CO2
Lean & Smyth
(2010)
ASEAN
1980-2006
CO2, EG,
electricity
consumption
EKC, Granger
Causality Test
CO2→
electricity
consumption CO2→ EG
Mohapatra & Giri
(2015)
India
1971-2012 CO2, EG, EC,
TO, UR, GFCF
ARDL,
Granger Causality
Test
EC → CO2
Narayan &Narayan (2010)
Malaysia 1980-2004 CO2, EG Cointegration EG effects on
CO2
Niu et al. (2011) Eight Asian-
Pasific
1971-2005
CO2, EG, EC
Cointegration,
Granger Causality Test
CO2→ EG
LAÜ Sosyal Bilimler Dergisi (VIII-II) EUL Journal of Social Sciences
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Öztürk &
Acaravcı (2010)
Turkey
1968-2005 CO2, EG, EC,
LF
ARDL,
Granger Causality
Test
All variable
co-integrate
Öztürk & Öz
(2016)
Turkey
1974-2011 CO2, EG, EC,
FDI
Cointegration,
Granger Causality Test
EC → EG CO2→ EC
Pao & Tsai
(2010)
BRIC countries
1971-2005 CO2, EG, EC EKC,
Granger Causality CO2 ↔ EC CO2 → EG
Salahuddin et al.
(2015)
Gulf
Cooperation
Council
1980-2012
CO2, EG, EC, FD
Cointegration,
Granger Causality
EC → CO2
CO2 ↔ EG
Tang & Tan
(2015) Vietnam 1976-2009
CO2, EG, EC,
FDI
EKC, Granger
Causality Test CO2 ↔ EG CO2 ↔ EC
Tiwari
(2011)
India
1971-2005
CO2, EG, EC
Cointegration,
Granger Causality Test
CO2 → EG CO2 ↔ EC
Xiongling (2016)
China
1961-2010
CO2, EG
Cointegration,
Granger Causality Test
EG → CO2
Yavuz (2014) Turkey 1960-2007 CO2, EG, EC EKC,
Cointegration CO2, EG and
ECcointegration
Wang et al. (2011)
China 1995-2007 CO2, EG, EC Granger
Causality Test CO2 ↔ EC
CO2: Carbon Dioxide Emissions PSE: Primary School Enrollment POP: Population
EC: Energy Consumption SSE: Secondary School Enrollment UR: Urbanization EG: Economic Growth TSE: Tertiary School Enrollment LF: Labor Force
TO: Trade Openness GFCF: Gross Fixed Capital Formation INF: Inflation Rate
IT: International Tourism TE: Technical Efficiency
FDI: Foreign Direct Investment FD: Financial Development
Different results appear in different studies because of the different variables,
different models, different data, and different methods used and different countries
included. In those studies the mostly used methods are ARDL and Granger causality
tests in both cross country panel studies and time series estimations.
We used electricity consumption instead of energy consumption since electricity
consumption has the highest share in total energy consumption in Turkey. Also the
shares of imports and exports of manufacturing industries in GDP is used instead of
the share of total imports and exports in GDP since manufacturing industry to be able
to investigate the impact of the manufacturing trade on CO2 emissions. To our
knowledge, there is no study in the literature integrating those variables in one
analysis. It should also be mentioned that the data used in this study covers longer
time period than the previous studies applied for the case of Turkey.
2. DATA AND METHODOLOGY
In this paper, the impact of electricity consumption, economic growth and trade
openness on CO2 emissions in Turkey by employing a time series data covering the
years from 1962 to 2013 collected from World Bank Development Indicators. The
long-run interaction between the dependent (CO2) and independent variables are
estimated by employing the econometric model represented by Equation (1). All
variables are in natural logarithms.
lnCO2= β0 + β1lnEC + β2lnGDP + β3lnTO + ɛ (1)
LAÜ Sosyal Bilimler Dergisi (VIII-II) EUL Journal of Social Sciences
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156 | The Impact of Turkish Manufacturing Industry on CO2 Emissions
In equation (1) β0 is the constant term and β1, β2, β3 are the long-run elasticities
with respect to electric power consumption, per capita GDP and trade openness. ɛ is
the error term and ln indicates that general logarithmic form of the variables. CO2 denotes carbon dioxide emissions per capita, while EC is electric power consumption
(kWh per capita) which is equal to total net electricity generation plus electricity
imports minus electricity exports minus electricity distribution losses. GDP is real
GDP per capita calculated by the 2005 US$ prices. GDP calculated as GDP divided
by population. To indicate trade openness which is calculated as the sum of
percentage of manufacturing exports and percentage of manufacturing imports to
GDP as suggested by Yanıkkaya (2003) and the subscript t represents the time
period.
3. EMPIRICAL ANALYSES
3.1. Unit Root Tests
In the time series analyzes, firstly, the stability levels of the series should be
determined. Non-stationary creates problem of spurious regression (Granger &
Newbold, 1974). So, Augmented Dickey Fuller (ADF) (1981), Phillips-Perron (PP)
(1988) and Kwiatkowski-Phillips-Schmidt-Shin (KPSS) (1992) unit root tests are
applied to test for stationarity of the series. Table 3 illustrates test results of
stationarity of ADF, PP and KPSS for CO2 emissions, GDP, electricity consumption
and trade openness.
Table 3: Unit Root Test Result: with intercept
Variables lnCO2 lnEC lnGDP lnTO
ADF I(1)* I(1)* I(1)* I(1)*
PP I(1)* I(1)* I(1)* I(1)*
KPSS I(1) I(0) I(1) I(1)
* and ** denotes the statistical significance at the 1% and 5%, levels respectively.
ln CO2, lnEC, lnGDP and lnTO are stationary both in ADF and PP tests at I(1).
According to KPSS test results; all variables are stationary at mix levels. Since
variables are stationary at mix level, ARDL approach is applied under bounds test in
this study the investigate long run relationship among variables.
3.2. Bounds Test
Bounds test is developed by Pesaran and Shin (1995), Pesaran et al., (1999,
2001) under the ARDL approach which estimates the long run interaction among the
variables. If all variables are stationary at same level, Engle-Granger (1987),
Johansen (1988, 1991) and Johansen-Juselius (1990) cointegration tests can be
applied to determine the long-run relationship between the variables. Pesaran et al.
(2001) proposed the ARDL approach for testing the relationship between different
levels of integrated variables (Verma, 2007; Esen, et al., 2012).
The ARDL approach is based on the least squares method. The main advantage
of the ARDL model is that with mix order of integration of variables at either I (1) or
I (0) it can be applied for cointegration test and the obtained results will be
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𝑖=1 𝑖=0
meaningful. In this study the variables are stationary at mix levels so that ARDL test
is employed to estimate long run interaction among variables.
According to the unit root test results the regressors have mixed ordered of
integration, therefore, Bounds tests based on ARDL approach represented by the
following model will be estimated with this respect:
∆ln𝐶𝑂2𝑡 = 𝛼0 + ∑𝑝 𝛼1𝑖 ln𝐶𝑂2𝑡−𝑖
𝑝 𝑖=0 𝛼2𝑖 ln𝐸𝐶 𝑡−𝑖 + ∑𝑝
𝛼3𝑖ln𝐺𝐷𝑃𝑡−𝑖 + 𝑝 𝑖=0 𝛼4𝑖 ln𝑇𝑂 𝑡−𝑖 + 𝜀𝑡 (2)
Where, α’s are the dynamic coefficients of the attached variables in long-run and
εt is an error term.
ARDL approach under the Bounds test results follows F-distribution. The critical
values for Bounds test is developed by Narayan and Narayan (2005) and Pesaran and
Timmermann (2005) which follow F distribution. If F-statistics for bounds test
exceeds the upper bound of critical value the null of no long run relationship between
the variables is rejected. If F-statistics for bounds test is estimated to be lower than
the lower bound of critical value the null hypothesis is not rejected. If F-statistics for
bounds test falls between lower and upper bounds than the analysis is said to be
inconclusive. This is stage one is necessary step to check whether exist a long run
relationship between the variables under investigation is tested by computing F-
statistics for the significance of the lagged levels of the variables in the error
correction form of the underlying ARDL model. The F-statistics confirms that there
is a cointegrating relationship based on the three models.
Bounds test considers five different cases. First case is applied without intercept
and trend, second case is applied with restricted intercept and without trend, Third
case is applied without deterministic unrestricted intercept and without trend, Fourth
case is applied by including the deterministic unrestricted intercept and restricted
trend and the last case is applied with unrestricted intercept and restricted trend. In
this study, we focused on the results of only the last three since they give more
reliable results (Katırcıoğlu et al., 2013).
Table 4 shows critical values of bounds test and table 5 shows the bounds test for
level relationship among variables.
Table 4: Critical Values of Bounds Test
Significance I(0) I(1)
0.01 3.65 4.66
0.05 2.79 3.67
0.10 2.37 3.2
F statistic : 7.9588
+ ∑
∑
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158 | The Impact of Turkish Manufacturing Industry on CO2 Emissions
𝑖=1 𝑖=0
Table 5: The Bounds Test for level relationship
Without deterministic
unrestricted intercept and no trend
With deterministic
unrestricted intercept and restricted trend
With unrestricted
intercept and restricted trend
Conclusion
Variables 𝐹𝑖𝑖𝑖 𝐹𝑖𝑣 𝐹𝑣 𝐻0
CO2/ EC, GDP, TO
2.700** 2.303*** 2.864** Rejected
** and *** denotes the statistical significance at the 5% and %10.
According to the Bounds test results, there is a long run relationship exist among
variables, which indicates EC, GDP and TO are in long run relationship with CO2 for
Turkey.
3.3. Error Correction Model
Error Correction Model (ECM) is developed by Engle-Granger (1987) stated
short-term imbalances when there is cointegration of the variables are established.
ECM coefficient shows the short run deviation from its long run equilibrium. ECM is
given below;
∆ln𝐶𝑂2𝑡 = 𝜆0 + ∑𝑝 𝜆1𝑖 ∆ln𝐶𝑂2𝑡−1
𝑝 𝑖=0 𝜆2𝑖 ∆ln𝐸𝐶 𝑡−1 + ∑𝑝 𝜆3𝑖 ∆ln𝐺𝐷𝑃𝑡−1
𝑝 𝑖=0 𝜆4𝑖 ∆ln𝑇𝑂 𝑡−1 + 𝜑𝐸𝐶𝑇𝑡−1 + 𝜁𝑡 (3)
Where λ is the parameter of error correction, ∆ is indicates the first differences
while the parameter ECTt−1 is the error correction term, φ is the speed adjustment
coefficient, ζ is the disturbance term in equation 3.
Table 6: ARDL approach long-run and short-run test results
Dependent Variable: ln𝐂𝐎𝟐
Long-run results
Variables Coefficient Standard Error p-value
ln𝐂𝐎𝟐 0.498 0.139 0.000
lnEC 0.722 0.213 0.001
lnGDP 0.391 0.174 0.007
InTO 0.002 0.001 0.119
Short-run results
Variables Coefficient Standard Error p-value
ECMT (-1) -0.334 0.045 0.000
Table 6 shows that long run and short run coefficients, whereas lnCO2 is taken as
the dependent variables. According to the results of ARDL approach lnEC, lnGDP
and lnTO have a statistically significant impact on lnCO2. It show that, when EC
increase by 100%, CO2 emissions will increases by 72.2 % and 100% increase in
+ ∑
+ ∑
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lnGDP leads to 39.1% increase in CO2 and when lnTO increase by 100%, CO2 emissions increasing 0.2%.
The estimation result of ECM is shown in Table 6. ECT (-1) coefficient is
statistically significant at 1% significance level and ECTt−1 is -0.334 with expected
sign, proposing that when emissions is under its equilibrium level, it adjusts by
almost 47% per year.
3.4. Granger Causality Test
If there is a long-term relationship between variables, causal relationship among
the variables should be estimated. Granger causality test using F statistic. Granger
causality is given as below;
∆𝐥𝐧𝐂𝐎𝟐𝐭
∆𝐥𝐧𝐄𝐂𝐭 ∝𝟏 ∝𝟐
∑𝐩
𝛃𝟏𝟏𝐢 𝛃𝟏𝟐𝐢 𝛃𝟏𝟑𝐢 𝛃𝟏𝟒𝐢 𝛃𝟏𝟓𝐢 𝛃𝟐𝟏𝐢 𝛃𝟐𝟐𝐢 𝛃𝟐𝟑𝐢 𝛃𝟐𝟒𝐢 𝛃𝟐𝟓𝐢
∆𝐥𝐧𝐂𝐎𝟐𝐭−𝐢
∆𝐥𝐧𝐄𝐂𝐭−𝐢
∆𝐥𝐧𝐆𝐃𝐏𝐭 [ ∆𝐥𝐧𝐓𝐎𝐭 ]
𝛗𝟏 𝛗𝟐
= [∝𝟑] +
∝𝟒 𝛆𝟏 𝛆𝟐
[ ] 𝛃𝟑𝟏𝐢 𝛃𝟑𝟐𝐢 𝛃𝟑𝟑𝐢 𝛃𝟑𝟒𝐢 𝛃𝟑𝟓𝐢
𝛃𝟒𝟏𝐢 𝛃𝟒𝟐𝐢 𝛃𝟒𝟑𝐢 𝛃𝟒𝟒𝐢 𝛃𝟒𝟓𝐢
+ ∆𝐥𝐧𝐆𝐃𝐏𝐭−𝐢 [ ∆𝐥𝐧𝐓𝐎𝐭−𝐢 ]
[𝛗𝟑] 𝐄𝐂𝐌𝐭−𝟏 + [𝛆𝟑
] (4)
𝛗𝟒 𝛆𝟒
The ∝’, β’s and φ’s are the parameters are estimated. ECMt−1 represents the one
period lagged error-term derived from the cointegration vector and the ε’s are
serially independent with mean zero and finite covariance matrix in Equation 4.
Table 7: Granger F-test results
∆ln𝐂𝐎𝟐 ∆lnEC ∆lnGDP ∆lnTO
∆ln𝐂𝐎𝟐 (3.232)** (0.379) (0.630)
∆lnEC (0.000) (0.292) (2.788)***
∆lnGDP (0.527) (0.463) (2.383)***
∆lnTO (2.594)*** (1.998) (2.625)***
x→y means x Granger causes y.
** and *** denotes the statistical significance at the 5% and %10.
The Granger causality results are represented in Table 7 The numbers in the table
represents F-statistic test results. The numbers in parentheses give the probability of
F-statistic. According to Table 7; there are three unidirectional granger causality
relationships exist among variables running from electricity consumption to CO2 emissions, from CO2 emissions to trade openness, and from trade openness to
electricity consumption. In addition to the unidirectional causal relationships, the test
results indicate that there is one bi-directional causality relationship exists among
variables, between trade openness and GDP per capita. Figure 1 illustrates granger
causality relationship among the variables.
𝐢= 𝟏
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Figure 1: Granger Causality Relationship between the Variables
3.5. Cusum and Cusumsq Test
The Cusum and Cusumsq test are applied to test the stability of the long term
coefficients used to obtain ECM, since instability problem might be the result of
incomplete modeling of short-run dynamics (Laidler, 1993). According to the test
results it can be stated that the estimated coefficients are stable in the long run since
the plots of both tests fluctuate inside the 5% critical bounds. Figure 2 shows the plot
of Cusum and Cusumsq Tests.
Figure 2: Cusum and Cusumsq Tests
20
15
10
5
0
-5
-10
-15
-20
1975 1980 1985 1990 1995 2000 2005 2010
1.4
1.2
1.0
0.8
0.6
0.4
0.2
0.0
-0.2
-0.4
1975 1980 1985 1990 1995 2000 2005 2010
CUSUM of Squares 5% Significance
CO2 Emissions Electricity
Consumption
GDP Trade Openness
CUSUM 5% Significance
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Zeliha Özdemir, Demet Beton Kalmaz | 161
CONCLUSION AND POLICY RECOMMENDATIONS
This papers aims to investigate the interaction between CO2 emissions, electricity
consumption, economic growth and trade openness for the case of Turkey by using
time series data covering the years between 1962 and 2013.
To be able to investigate the interaction among variables the empirical analysis
employed starting with the tests for stationary of the variables. Since the variables
show mix order of integration, the bounds test based on ARDL approach is employed
to estimate the long run relationship among the variables. According to the Bounds
test results it is found that the electricity consumption, economic growth and trade
openness have statistically significant and positive impact on CO2 emissions.
ECM applied to the short run deviation from its long run equilibrium. The
estimated ECT (-1) coefficient of the employed ECM is statistically significant at 1%
significance level with expected sign, proposing that when CO2 emissions is under its
equilibrium level, it adjusts by almost 33% per year.
Then, the found that long-term relationship among variables, therefore Granger
Causality Test applied. The Granger Causality Test results demonstrated the
existence of unidirectional short-run causal relationship from electricity consumption
to CO2 emissions, from CO2 emissions to trade openness, from trade openness to
electricity consumption. Additionally, there is evidence of one bi-directional
causality relationships between trade openness and GDP per capita.
Cusum and Cusumsq Test applied to coefficients are stable in the long run.
Cusum and Cusumsq Test results are evidence that coefficients in ECM are stable
over the period between 1962 and 2013.
Estimation results show that as electricity consumption increases CO2 emissions
also increase in case for Turkey. The main reason behind the increase in CO2 emissions is due to the use of fossil fuels for electricity generation since fossil fuels
have the highest share among the energy resources use to generate electricity in
Turkey. Turkey’s energy policy has a critical importance both in reducing the
environmental problems caused by CO2 emissions and in terms of economic growth.
Turkey’s energy production depends highly on foreign countries energy sources
since energy production in manufacturing sector is generated from electricity, which
is produce mostly from natural gas imported from abroad increasing cost of
production.
Turkey is one of the countries which generate highest levels of CO2 emissions.
High level of CO2 emissions depends on two reasons. First is that Turkey has high energy intensity arising from inefficient use of energy (Islatince & Haydaroğlu,
2009) and second is the dependency of Turkey on non-renewable sources instead of renewable energy sources to generate in energy, in particular electricity. Electricity is one of the main inputs in industrial manufacturing, and it is also a fundamental factor
that increases people's quality of life (Karagöl, et al., 2007). The priority of Turkey
should be to decrease energy intensity and increase the share of renewable energy
sources to generate electricity in the manufacturing industry. This can be achieved
through carbon taxation of the manufacturing sector. The carbon tax system can be
designed to promote the use of renewable energy sources to generate electricity for
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162 | The Impact of Turkish Manufacturing Industry on CO2 Emissions
the manufacturing sector. This will also decrease the importation of natural gas.
Thus, the cost of electricity generation will be decreased. Moreover, the cost of the
manufacturing industry production will be reduced in long-run.
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Zeliha Özdemir, Dönüşüm İş Sağlığı ve Güvenliğinde İnsan Kaynakları Uzman
Yardımcısıdır. Aldığı eğitim sırasıyla, Muhasebe ve Vergi Uygulamaları Ön
Lisans (Afyon Kocatepe Üniversitesi, Türkiye), Ekonomi Lisans (Lefke Avrupa
Üniversitesi, KKTC), İşletme Yüksek Lisans (Lefke Avrupa Üniversitesi, KKTC).
Uluslararası kongrede bildiri sunan Özdemir'in ilgi alanları şunlardır: Genelde
Ekonomi özelde ise Enerjidir.
Zeliha Özdemir, is an Assistant of Human Resource Management in
Transformation Health Safety Environment. Her education is respectively
Associate Degree of Accounting and Tax Practices (University of Afyon
Kocatepe, Turkey), Bachelor of Economics (European University of Lefke,
TRNC), Master of MBA (European University of Lefke, TRNC). She has a paper
presented in an international congress. Her research interests consist of
economics and energy.
Asst. Prof. Dr. Demet Beton Kalmaz, is a lecturer in European University of
Lefke of the Faculty of the Economics and Administrative Sciences. Her
education is respectively Bachelor of Sociology (University of Hacettepe,
Ankara, Turkey), Master of Economics (University of Leeds, Leeds, UK), and
PhD. in Economics (Eastern Mediterranean University, Famagusta, TRNC).
She has several papers presented in national and international congresses and
articles published. Her research interests consist of energy, labor market and
general economics topics.
Yrd. Doç. Dr. Demet Beton Kalmaz, Lefke Avrupa Üniversitesi Ekonomi
Bölümü öğretim üyesidir. Aldığı eğitim sırasıyla Sosyoloji Lisans (Hacettepe
Üniversitesi, Ankara, Türkiye), Ekonomi Yüksek Lisans (University of Leeds,
Leeds, UK), ve Ekonomi Doktora’dır (Doğu Akdeniz Üniversitesi, Mağusa,
KKTC). Ulusal ve uluslararası kongrelerde bildiri sunan ve makale çalışması
bulunan Kalmaz'ın ilgi alanları şunlardır: Genelde ekonomi özelde ise enerji,
emek piyasası ve uluslararası ekonomi konularıdır.